Abstract
Population growth, rising income and urbanization have fueled a significant increase in demand for animal products in developing countries since the early 1970s. The phenomenon, dubbed as the Livestock Revolution, is anticipated to slow down in the coming decades, except in Africa where the Revolution is expected to continue and urbanize. This paper examines the urbanization of the Livestock Revolution in Africa. It estimates that in 2050 almost 70% of total meat and milk consumption will likely come from cities, with urban dwellers demanding, compared to today, 28 and 47 additional million metric tons of meat and milk, respectively. The consequent transformations of the livestock value chain serving urban and peri-urban areas may pose unprecedented public health and environmental challenges to policy-makers.
Keywords: Africa, Rural-urban consumption, Animal source food, Urbanization
Highlights
-
•
Between 2015 and 2050, meat and milk demand should respectively triple and double in Africa.
-
•
In 2050, almost 70% of meat and milk demand in Africa should come from urban areas.
-
•
The number of mid- and large-scale livestock operators in peri-urban areas will likely increase.
-
•
Urban and peri-urban areas could be veritable hotspots for zoonotic diseases.
1. Introduction
The population of Africa is projected to almost double reaching about 2.5 billion people in 2050. More than 80% of that increase should occur in cities, with about 1.5 billion Africans living in urban areas by 2050. Economic growth is also expected to keep its pace, supporting major increases in consumer purchasing power. Sustained population growth, coupled with changes in consumption patterns due to rising real per capita income and urbanization, underpins what Delgado et al. in 1999 dubbed the Livestock Revolution. The term, Livestock Revolution, was coined to describe the significant increase in demand for animal-sourced foods (ASFs) that started in developing countries at the beginning of the 1970s and continued in the new millennium (see Fig. 5). The term also captures the associated implications on livestock production systems, environment and public health.
A wealth of literature exists on the determinants of the demand of ASFs. On the one hand, as purchasing power increases, consumer food preferences shift towards higher quality and more diversified diets, in which ASFs are a key component. (Colen et al., 2018; Skoufias et al., 2011). On the other hand, urban residents not only have different lifestyles than rural dwellers – for example they are more sedentary, members of a two-income family and usually employed in either the industry or the service sector – but also have access to wider food options and infrastructure that facilitates transporting and storing perishable food products, such as milk and meat (Cockx et al., 2018; Hawkes, 2008; Regmi and Dyck, 2001). Many studies have therefore found a positive correlation between urbanization and per capita consumption of animal products (Delisle et al., 2012; Rae, 1998; Worku et al., 2017), though opposite evidence also exists (Abdulai and Aubert, 2004; Cockx et al., 2018).
The significant growth in ASF consumption in developing countries between 1973 and 2013 – a six- and four-fold increase in meat and milk consumption, respectively – brought on a parallel increase in production, with developing countries accounting in 2013 for 63% and 53% of the total world's meat and milk production, respectively, versus 31% and 22% forty years earlier (FAO, 2018b). A larger herd and higher animal productivity contributed to increased livestock production, which was also characterized by land-use conversion from forests to pastures for large ruminants, particularly in Latin America, and the emergence of mid and large-scale poultry, pig and dairy producers around urban and peri-urban areas, which moved afield only as urbanization intensified (FAO, 2013; Steinfeld et al., 2006; Steinfeld. H., 2019; Thornton, 2010). As a consequence, the effects of livestock production on the environment, such as through greenhouse gas emissions, and public health, such as through zoonotic diseases that jump from animals to humans, have become increasingly pronounced (FAO, 2013; Jones et al., 2008; Steinfeld et al., 2006).
In the coming three decades the Livestock Revolution is anticipated to slow down, as developing countries should experience slower growth rate of population, urbanization and GDP per capita than in the past forty years. The exception will likely be Africa, where the Livestock Revolution might continue unfolding but with a peculiar feature with respect to the past: it is expected to be urban. With the number of people living in urban areas skyrocketing, even a small rise in per capita consumption would translate in a very large increase in aggregate demand of ASFs, which may pull livestock production system closer to urban areas, as historical evidences from Asia and Latin America suggest (Steinfeld et al., 2006). An urbanized Livestock Revolution will likely have profound and unprecedented effects on the development trajectory of the livestock sector, with major consequences on the environment and public health.
This paper examines the urbanization of the Livestock Revolution in Africa and discusses its implications on livestock production systems and value chains. It relies upon FAO's long-term demand and supply projections of ASFs (FAO, 2018a) in Africa under a “business-as-usual” (BAU) scenario, which assumes no structural change with respect to the past, on the World Bank Global Consumption Database (2007), which provides information on per capita expenditure of livestock products by rural and urban areas, and on the United Nations (UN) World Urbanization Prospects (UNDESA, Population Division, 2018) that provide long-term projections on rural and urban population by region and country.
Section 2 presents long-term trends in ASF consumption in Africa, with a focus on the aggregate rather than per capita demand as the former, more than the latter, will likely prompt changes of interest in livestock production systems and value chains. Section 3 estimates meat and milk consumption in urban and rural areas in 2050; to our knowledge neither projections nor forecasts are available on consumption of livestock products by urban and rural areas in the future. Section 4 discusses the likely transformations of the livestock production systems and value chains in response to the urbanized Livestock Revolution and the associated environmental and public health consequences. Section 5 draws conclusions.
2. The Livestock revolution continues
Between 1973 and 2013 total consumption of meat and milk in developing countries increased by 161 and 281 million metric tons, respectively. In the developed world, consumption of meat and milk grew by 33 and 57 million metric tons, respectively. Over the same period, per capita consumption of meat tripled in developing countries, reaching 34 kg/year in 2013, while milk consumption more than doubled from 29 to 63 kg/year. Percentage increases in per capita consumption in the developed world have been instead contained, both due to the already high protein intake and an increased preference toward diets with reduced consumption of ASFs (Annex I).
In the last four decades, the Livestock Revolution did not occur uniformly across the developing world (Delgado et al., 2001; Pica-Ciamarra and Otte, 2011): China and Brazil accounted for about 59% of the total increase in meat consumption, while India, China, Pakistan and Brazil contributed 67% to the total increase in milk consumption. Though the population size of these countries largely explains this trend, increases in per capita consumption were also overwhelming. For example, in 1973, China's per capita consumption of milk was 2 kg/year and reached 32 kg/year in 2013.
Africa contributed little to the Livestock Revolution between 1973 and 2013. Although the proportion of developing countries’ population living in Africa increased from 14% to 19%, Africa contributed only 9% and 11% to the total increase in meat and milk consumption in the developing world. On the continent, meat and milk consumption grew by 14 and 32 million metric tons, respectively. In 1973, per capita meat consumption in Sub-Saharan Africa (SSA) and Northern Africa was 13.7 and 12.6 kg/year, respectively; it grew to 16.2 kg/year and 27.8 kg/year in 2013. Similarly, between 1973 and 2013 per capita milk consumption increased from 28 to 30 kg/year in SSA and from 44 to 92 kg/year in Northern Africa (Annex I).
FAO's long-term consumption projections (2018a) suggest that in the next decades total and per capita consumption of ASFs in developing countries, with the exclusion of Africa, will likely grow at a substantially lower annual rate than in the previous 40 years (Annex I). After all, in developing countries (excluding Africa), total and urban population are projected to grow by 0.6% and 1.4% per year, less than half of the annual growth rates for the 1973–2013 period. GDP per capita, which more than tripled in the first period, should about double by 2050.
Conversely, the drivers of the Livestock Revolution are expected to continue exercising their influence in Africa. Between 2013 and 2050, the African population is projected to grow by 2.2% per year vis-à-vis an annual growth rate of 2.7% over the 1973–2013 period. In 2050, close to 60% of the population will likely be urban vis-à-vis 40% in 2013 and 24% in 1973 (UNDESA, Population Division, 2018). These trends are expected to be more pronounced in SSA, where urban population should almost quadruple in the next three decades, reaching 1.2 billion in 2050. Finally, GDP per capita in Africa is expected to double by 2050, while it grew by 36% over the 1973–2013 period.
A veritable Livestock Revolution is therefore expected to unfold in Africa in the next decades. In particular, in SSA, aggregate meat and milk consumption are projected to growth at 3.4% and 2.9% per year (vis-à-vis 1% in the other developing regions), with both absolute and relative increases in per capita consumption higher in the coming decades compared with the past 40 years (Annex I).
What matters the most, however, is that the coming Livestock Revolution in Africa differs from any past development trajectory. Fig. 1 displays indexed series for urbanization, GDP per capita and aggregate meat consumption in Africa and Eastern Asia, which is the region that experienced the largest changes in meat consumption over the past decades (Pica-Ciamarra and Otte, 2011). Three main features emerge from the comparison of the trends in these regions.
First, the growth rate in meat consumption in Africa for the 2013–2050 period is expected to be similar to that experienced by Eastern Asia during the peak of the Revolution, as the slopes of the two lines representing aggregate meat consumption do not differ significantly. In Africa, the aggregate increase in meat demand for the 2013–2050 period (+38 million metric tons) should be 2.7 times higher than the increase in the previous decades (+14 million metric tons). Today, African livestock production is unable to satisfy local demand, with about one third of all countries in the continent importing more than 20 percent of their total meat supply. The projected increase in aggregate meat demand, therefore, will likely exacerbate pressures on livestock production systems and may increase the African dependence on imports.
Second, Africa will have to respond to this production challenge while facing a massive urbanization process. The growth rate in urban population, already higher in Africa than in Eastern Asia over the period 1973–2013, is projected to remain significantly higher also in the coming decades, as shown in Fig. 1. In Eastern Asia, the urban population increased by 666 million between 1973 and 2013; in Africa, it is estimated to increase by more than 1 billion between 2013 and 2050.
Last but not least, Africa will likely have less resources available on a per capita basis than Eastern Asia to manage a sustainable transformation of the Livestock Sector (Annex VI). In 1973, GDP per capita in Eastern Asia was 1.8 times higher than in Africa and, since then, has grown and is projected to grow at a much faster rate. African decision-makers, therefore, may face unprecedented challenges in managing the coming Livestock Revolution on the continent.
3. Africa: the Livestock revolution urbanizes
The projected massive increase in ASF consumption in Africa calls for a better understanding of the contribution of urbanization to the Livestock Revolution for informed policy decisions. The way livestock production systems and value chains adjust in response to a growing demand for ASFs, in fact, depends not only on the total quantity but also on the location where the demand occurs. To our knowledge, neither forecasts nor projections exist on the future consumption of ASFs in urban versus rural areas in Africa. This section provides estimates of the future demand for livestock products in African urban areas.
3.1. Data
To estimate the projected quantity of livestock products consumed in urban versus rural areas, we use three sets of data: the FAO long-term consumption projections (2018a), the World Bank Global Consumption Database (2007) and the UN World Urbanization Prospects (2018).
FAO (2018a) provides 5-year interval estimates for the aggregate consumption of beef and veal, pork, small ruminant meat, poultry meat and milk by country for the 2015–2050 period. FAO projections are based on two economic models: (i) the FAO Global Agriculture Perspectives System Model (Kavallari et al., 2016), a partial equilibrium model that, starting from FAOSTAT food balance sheets for 2012, projects supply, demand and prices for agricultural commodities (crops, processed good, and livestock products) by adjusting simultaneously variables such as crop yields, land requirements and animal herd size by livestock production system, and balancing the global market up to the year 2050; and (ii) the Environmental Impact and Sustainability Applied General Equilibrium Model (Mensbrugghe, 2010), a general equilibrium model that simulates the interactions between the different economies, including their agricultural sector, and the global environment as affected by greenhouse gas emissions or global mean temperature. FAO (2018a) produced projections for three scenarios (“towards sustainability”, “business-as-usual” and the “stratified societies”). Here, we use the projections from the “business-as-usual” scenario, which assumes no major structural break with respect to past trends of food preferences and food waste at consumer level. As the FAO database does not contain country-level data for Burundi, the Democratic Republic of the Congo, Eritrea, Libya, Somalia, and Sudan, we imputed projected values using the average per capita consumption of neighboring countries with comparable level of development (GDP per capita projections are also sourced from FAO (2018a)).
The World Bank Global Consumption Database (2007) draws on 77 national household consumption or expenditure surveys conducted between 2000 and 2011 in Africa, Asia, Europe, and Central and Latin America. It presents summary statistics on consumer spending patterns, expressed in 2010 values, for a variety of food and non-food items at national level and by rural and urban areas. As the relation between urban and rural per capita consumption depends on the level of development of the survey year, we generate estimates for the survey year by multiplying the database values by the ratio of the household final consumption expenditure per capita in the survey year to the corresponding value in 2010. To allow for cross-country comparison, we convert local currencies into international dollars adjusted for purchasing power parity (2011 PPP).
The UN World Urbanization Prospects are the official UN estimates and projections of rural and urban population by country and region (UNDESA, 2018). Projections are based on the most recent available population censuses. The dataset does not use its own definition of urban, but follows the definitions used by the different countries. For example, in Ethiopia localities with more than 2000 inhabitants are considered urban, while in Burkina Faso all administrative centers of provinces (total of 45) plus 4 medium-sized towns are considered as urban areas (UNDESA, 2018).
3.2. Methods
To estimate the consumption of livestock products originating from urban dwellers, we first use the World Bank Global Consumption Database (2007) to calculate the rural to urban expenditure ratio of selected ASFs. We then use the estimated expenditure ratio to split the FAO country-level projections of ASF consumption into rural and urban consumption. In particular, under the hypothesis that the ratio between total rural and urban consumption in country j is primarily explained by the level of development (GDP per capita) and the share of population living in urban areas (urban share), we use equation (1) to estimate the relation between per capita rural expenditure () and per capita urban expenditure () for each livestock commodity (i: beef and veal, pork, small ruminant meat, poultry meat and milk). We control for regional fixed effects by grouping the countries in 12 regions (Central, Eastern, Western, South-Eastern and Southern Asia; Northern and Sub-Saharan Africa; Northern, Eastern and Southern Europe; Caribbean and Central America; South America). In all cases, the Breusch-Pagan test (Breusch and Pagan, 1979) detects heteroskedasticity, i.e. the variance of the error term is not constant across observations causing inefficiency of the estimates. We use ordinary least squares and the Huber-White robust sandwich estimator for all equations to correct for heteroskedasticity (Huber, 1967; White, 1980).
(1) |
The functional form is specific for each livestock commodity, with the selection of both the explanatory variables and the interaction terms guided by the Akaike's information criterion (Akaike, 1973), Bayesian information criterion (Schwarz, 1978), the statistical significance of the parameter and the variance inflation factor (VIF) (Verbeek, 2008).
Based on the predictions of the fitted models, we estimate the marginal effects (i.e. margins of derivative of response - ) and the elasticity of urban expenditure on ASFs () at different level of GDP per capita and share of urban population (U) as follows:
(2) |
(3) |
The combination of equations (2), (3) allows estimating the rural to urban expenditure ratio (), as:
(4) |
The expenditure ratio (equation (4)) depends on the country's economic development, proxied by GDP per capita and urbanization. A ratio equal to 1 implies equal per capita expenditure for product i in rural and urban areas. A ratio greater than 1 implies a lower per capita expenditure in urban areas. We use the estimated ratios to calculate the urban consumption of beef and veal, pork, small ruminant meat, poultry meat and milk for each African country j as follows:
(5) |
where is the FAO projected aggregate consumption of product i in country j; and are the population living in rural and urban areas in country j, respectively.
3.3. Regression results
Table 1 reports the results of regressions for each livestock commodity as well as the specification of equation (1), i.e. the selected explanatory variables. Note that the share of population living in urban areas was excluded as a stand-alone regressor or as an interaction variable in two out of the five estimated equations as its inclusion did not significantly increase the explanatory power of the model and caused high values for VIF, i.e. urban population share was highly correlated with at least one of the other predictors in the model. Regional fixed effects were found significant only for pork and poultry meat.
Table 1.
beef and veal | pork | small ruminant meat | poultry meat | milk | |
---|---|---|---|---|---|
urban expenditure | 0.597*** | 1.467*** | 1.193*** | 0.234*** | 0.508*** |
(0.11) | (0.20) | (0.18) | (0.07) | (0.09) | |
urban exp*GDP per capita | 0.028*** | −0.067*** | 0.015* | 0.021** | |
(0.01) | (0.01) | (0.01) | (0.01) | ||
urban share*urban expenditure | −0.393 | ||||
(0.23) | |||||
GDP per capita*urban share | 0.647* | 0.419* | |||
(0.27) | (0.17) | ||||
D(Southern Europe) = 0*urban exp | −0.489* | ||||
(0.20) | |||||
D(Northern Europe) = 0*urban exp | −0.371*** | ||||
(0.05) | |||||
D(South America) = 0*urban exp | 0.347*** | ||||
(0.07) | |||||
Observations | 76 | 65 | 69 | 77 | 76 |
Adjusted R-squared | 0.920 | 0.967 | 0.856 | 0.920 | 0.894 |
Standard errors in parentheses.
*p < 0.05, **p < 0.01, ***p < 0.001.
Note: Urban and rural expenditure are per capita values in current international $ (2011 PPP) from the World Bank Global Consumption Database. GDP per capita, expressed in 1000$ (2011 PPP), is from the World Bank's World Development Indicators database; urban population share data are from UNDESA Population Division, World Urbanization Prospects: The 2018 Revision, table 21. D(region name) are dummy variable for the regions.
Based on the predictions of the fitted models, we calculated the rural to urban expenditure ratio for different animal products (equation (4)). Results are similar for all products, but for small ruminant meat (Fig. 2 ).
At low levels of GDP per capita, per capita expenditure in rural areas for beef and veal, poultry meat, and milk is about half of that in urban areas. As per capita GDP increases, the per capita expenditure in rural and urban areas converges, though it always remains higher for urban dwellers. This pattern is similar for per capita expenditure on pork, though at high level of GDP and/or urban share people in rural areas may spend more on pork than their urban counterparts. In particular, the rural/urban expenditure ratio is higher than 1 when GDP per capita is higher than 3600 USD and the urban population is at least 88%, or when the urban population is more than 28% and GDP per capita is at least 11,500 USD. For per capita expenditure on small ruminant meat, the rural/urban expenditure ratio decreases as GDP per capita goes up and increases with urbanization. In particular, with a GDP per capita lower than 5300 USD, rural households spend more on small ruminant meat than urban dwellers, regardless of the urbanization level. Conversely, with a GDP per capita higher than 10,200 USD, people in urban areas spend more than those in rural areas on small ruminant meat, even at low level of urbanization.
Different trends of the rural to urban expenditure ratio for small ruminant meat can be explained by the fact that rural households largely hold small ruminants as a source of financial security; demand for small ruminant meat is highly seasonal, with peaks around religious ceremonies and other celebrations; and consumption of small ruminant meat is highly responsive to price dynamics (CNFA, 2016; Abdulrahman 2017). Accordingly, as GDP per capita goes up, less rural households are expected to hold small ruminants, with a consequent reduction in self-consumption and increase in market demand. During demand peaks, prices will be higher and better-off urban dwellers will be likely to purchase more meat than their rural counterparts. That said, estimates of the rural to urban expenditure ratio for small ruminant meat should be taken with caution also noting that for GDP per capita higher than 18,000 USD and high level of urbanization, the ratio is highly unstable; we therefore truncated the results in Fig. 2. The weakness of the results may be due to the data underlying the model, as no clear relation between expenditure, GDP per capita and urbanization emerges (Annex II). The high seasonality of demand for small ruminant meat and the fact that some of the household surveys of the Global Consumption Database collected consumption data over a short period of time may partly explain this anomaly.
3.4. Urban and rural consumption in 2050
The 2050 consumption of beef and veal, pork, small ruminant meat, poultry meat and milk projected by FAO (2018a) for each African country was divided by rural and urban areas using equation (4). Results suggest that the Livestock Revolution in Africa should urbanize, with the demand for livestock products mainly originating from urban dwellers in the coming decades.
3.4.1. Consumption of meat in urban areas
In 2050, the aggregate consumption of meat originating from urban dwellers might more than triple with respect to today and should represent 69% of the total, though Africa will likely be only 59% urban. For all types of meat, the percentage increase in consumption is projected to be 3 times higher in urban than in rural areas. On the other side, increase in per capita consumption is expected to be more accentuated in rural areas (+30% or 3.9 kg/person between 2015 and 2050) than in urban areas (+11% or 2.7 kg/person between 2015 and 2050); thus, the consumption gap between rural and urban areas is expected to shrink. Nevertheless, in 2050 urban dwellers should still consume significantly more meat on a per capita base (27 kg/person/year vis-à-vis 17 kg/person/year in rural areas) (Table 2), with the only exception for small ruminant meat (Table 6 in Annex III).
Table 2.
Meat consumption (kg/person/year) |
Milk consumption (kg/person/year) |
|||||||
---|---|---|---|---|---|---|---|---|
Region | rural |
urban |
rural |
urban |
||||
2015 | 2050 | 2015 | 2050 | 2015 | 2050 | 2015 | 2050 | |
Africa | 13.1 | 17.1 | 24.2 | 26.9 | 33.1 | 33.8 | 57.9 | 49.9 |
Northern Africa | 20.8 | 28.4 | 30.8 | 37.6 | 72.8 | 77.5 | 123.3 | 120.3 |
Sub-Saharan Africa | 11.7 | 15.4 | 22.2 | 25.0 | 25.7 | 27.5 | 37.5 | 36.9 |
The gap between urban areas of Northern Africa and SSA is projected to widen. In fact, although aggregate urban meat consumption should more than double in Northern Africa and almost quadruple in SSA (Fig. 3), population growth will likely offset this difference: in 2050 urban dwellers in SSA are expected to consume 25 kg/person/year of meat (3 kg more than in 2015), vis-à-vis 38 kg/person/year in Northern Africa (up from 31 kg/person/year in 2015).
3.4.2. Consumption of milk in urban areas
Between 2015 and 2050 in Africa, urban consumption of milk is projected to grow by 2.6 times to account for 68% of the total milk consumption in the continent. This trend is largely explained by the growing urban population, as per capita consumption is expected to marginally decrease in cities (Table 2). Conversely, over the same period, per capita milk consumption in rural areas should slightly increase (+2%), resulting in a shrunk urban-rural gap, though per capita values should remain significantly lower in rural areas (34 versus 50 kg/person/year).
The increase in the aggregate urban consumption should mainly be led by SSA, where consumption might more than triple. Nevertheless, in per capita terms, the gap between SSA and Northern Africa is expected to remain significantly high, with people in Northern Africa consuming 3 times more milk on a per capita basis in 2050.
3.5. Sensitivity analysis
The results presented above have to be interpreted considering their potential limitations.
The hypothesis underpinning equation (5) is that the urban to rural expenditure ratio is equal to the ratio of the quantities consumed. This would be true if there were no price differences between urban and rural areas, which is not always the case (Cockx et al., 2018; Deaton and Dupriez, 2011; Gaddis, 2016). Because of high transportation cost and limited market integration, rural prices are often lower for unprocessed and locally produced food, and higher for processed and imported food products (e.g. Gibson (2009) for Vietnam and Nakamura et al. (2019) for Nigeria). Deaton and Dupriez (2011) found that differences in food prices between urban and rural areas decrease as economic development progresses because both transaction cost and self-production in rural areas reduce. In particular, they found that in India and Brazil urban food prices were about 10% and 3% higher than rural food prices respectively.
Furthermore, the statistics available in the Global Consumption Database of the World Bank – used to estimate the rural to urban ASF expenditure ratio–- include consumption of home-produced food as well as food received as gift: these are valued at farm-gate prices that are lower than retail prices. As self-consumption is higher in rural areas and, based on literature on spatial price differences mentioned above, prices in urban areas are likely higher for domestically produced livestock products, i.e. the model results for urban consumption of ASFs may suffer from overestimation.
However, Africa imports a non-negligible quantity of its domestic supply of meat and milk. For example, import values are significantly higher if compared with the share of the domestic supply imported in India and Brazil when the study of Deaton and Dupriez (2011) was carried out (Table 7 in Annex IV). Accordingly, given the importance of imported food, the pace of urbanization and the economic growth, we can expect a mild and decreasing spatial price difference over time.
Unfortunately, disaggregated price data for urban and rural areas are not readily available. Thus, to test the sensitivity of our results to price differences between rural and urban areas, we rerun the model under two alternative scenarios, i.e. with urban prices 3% and 10% higher than rural prices. Results hardly change: in 2050 the share of ASF consumption in urban areas would reduce by less than one and by between one and two percentage points if urban prices were higher by 3% and 10% than rural ones, respectively (Table 8 in Annex IV).
4. Discussion
The projected increase in ASF consumption in Africa should come mainly from urban centers: in 2050, urban dwellers are expected to contribute about 69% and 68% of the total consumption of meat and milk, respectively. We estimated that in 2015 about 56% and 55% of all meat and milk consumption originates in urban areas. Market transactions for ASFs should be even more skewed towards urban areas, because self-consumption is largely a rural phenomenon. Nationally representative survey data for Kenya, Ethiopia, Nigeria, Uganda and Burkina Faso suggest that, on average, urban households purchase at least 77% of the milk and 82% of the meat they consume. On the other side, households in rural areas purchase less than half of the milk they consume (with the exception of Nigeria) and between 47% and 88% of the meat consumed (Annex V). Therefore, if the average share of ASF self-consumption is excluded from the model results, the urban market for meat and milk would represent 74% and 82% of total market for ASFs, respectively.
The remarkable increase in demand for ASFs, coupled with a shift in its geography, is expected to trigger major transformations in African livestock production systems and value chains. Historical evidence suggests a process of production intensification should occur, with increased levels of productivity all along the livestock value chain (Thornton, 2010; OECD-FAO, 2009). Indeed, in 2015 the African Union launched the 2015–2035 Livestock Development Strategy for Africa whose aim is to transform “the prevailing subsistence livestock production systems … into vibrant market-oriented systems” through concerted policies and investments in breeding, feeding, water systems, animal health and marketing (African Union, 2015). However, based on FAO “business-as-usual” projections, net trade (i.e. domestic production net of demand for food and other uses) is projected to increase yearly by 3.9% for meat, despite a large expansion of production. Though, projections for milk production and demand should move Africa from a position of net importer in 2013 to net exporter in 2050. In all cases, the anticipated process of livestock production intensification, while varied by country and region, will be intertwined with the process of urbanization. In particular, when cities and towns grow and infrastructure in rural areas is limited, production of perishable food, including livestock, tend to be located close to consumption (Chamberlin and Jaybe, 2013; Migose et al., 2018; Steinfeld et al., 2006). Based on The World Bank logistic performance index, which measures the efficiency and quality of a country's logistics services, SSA scores last among the six world regions in five out of the six dimensions of the index. If one looks at the quality of trade and transport related infrastructure, 15 out of the bottom 20 countries are in Africa (World Bank, 2019).
Currently, only in 33% of all African districts households and farms need less than 1 h to reach the closest urban center; it takes more than 6 h for households in 20% of all districts to reach a town or city (Weiss et al., 2018). While being closer to markets reduces transaction costs for producers, land and labor are expected to be scarce and hence expensive production factors in urban and peri-urban areas. Thus, livestock operators in these locations will have incentives to intensify production and maximize their profit per unit of animal or labor (Duncan et al., 2013; Oosting et al., 2014).
As a response to the massive increase in the demand for ASFs in urban areas in the coming years, we expect therefore a growing number of market-oriented livestock operators, from small to medium -scale livestock farms, to emerge in and around cities and towns in the medium term. In the longer term – with growing availability of infrastructure and increased pressure on farmlands due to urban expansion – production may move afield (Seto and Ramankutty, 2016). Available evidence, though scattered, indicates that already today there is a significant number of livestock keepers in African urban and peri-urban areas, including subsistence and commercially-oriented producers (Amadou et al., 2012; Graefe et al., 2008; Muhammad, 2008). Furthermore, a large share of urban dwellers keep poultry, and ownership of small ruminants and dairy cattle is also common (Grace et al., 2015).
Data from nationally representative surveys for 12 SSA countries indicate that between 2% (Sierra Leone) and 49% (Niger) of all urban households keep cattle; between 15% (Malawi) and 71% (Senegal) small ruminants; and between 33% (Rwanda) and 84% (Mozambique) poultry (FAO, 2020). As a consequence, the density of livestock in urban areas is high. Census data for Kenya and Uganda, which allow accurate small area estimations, confirm that already today livestock density in urban and peri-urban areas is as high as that in rural areas, as shown in Fig. 4 (Kenya National Bureau of Statistics, 2009; Uganda Bureau of Statistics, 2010).
The urbanizing livestock revolution, therefore, will likely lead to an increased concentration of livestock and people in and around urban areas in the coming decades, which represents an emerging and worrisome environmental and public health challenge for the African continent. In particular, land-use change and increased animal density in urban areas might support novel and more frequent contacts between humans, domesticated animals and wildlife, thereby creating veritable hotspots for the emergence of zoonotic diseases (ZDs) (Hassell et al., 2017; Neiderud, 2015). An outbreak of a ZD originating in wild and/or domestic animals that jumps to humans might not only significantly impact livestock production, but also result in a high human death toll with broader disruptive impact on society. Eventually, it could trigger social unrest and destabilize governments by eroding public trust and confidence. If a ZD spreads rapidly across countries, it can also result in worldwide pandemics (Berry et al., 2018; Ayano Ogawa, 2019), as the recent Covid-19 pandemic is demonstrating. And because of both the increased risk of animal diseases as well as stiffer competition to access productive resources in urban and peri-urban areas, farmers could be tempted to imprudently use antibiotics not only to treat sick animals but also as a growth promoter and/or for prophylaxis. This, in turn, might contribute to antimicrobial resistance in humans which is an increasing threat to global health (Robinson et al., 2017).
In addition, the animal herds that are required to meet the sharp increase in demand will likely generate profound environmental impacts (Steinfeld et al., 2006). Livestock production systems in proximity to urban centers may pollute available water sources and, in water scarce areas, also generate social tensions. The same could happen with livestock production systems that require large land areas in the proximity of urban and peri-urban centers, which also contribute to raising land price.
It is worth noting that the growing demand for ASFs in urban areas also presents a major business opportunity for the livestock sector to develop sustainably and contribute to poverty reduction and food security (Cole et al., 2008). Lee-Smith (2010) even argues that the nutritional benefits of urban livestock-keeping outweighs any health risks, as the latter can be effectively managed if appropriate policies are in place.
The correlations between urbanization, livestock production systems and their ultimate impact on African society, including on public health, the environment and people's livelihoods, are complex, heterogeneous and shaped by a multitude of anthropogenic and agro-ecological factors. In the coming decades, because of the urbanizing Livestock Revolution, they will become increasingly complex and difficult to manage. However, urban and peri-urban livestock systems are not among the top priorities in the Africa policy agenda, at national, regional and continental level. For example, the 2015–2035 Livestock Development Strategy for Africa (African Union, 2015) considers the urbanization of the Livestock Revolution largely, if not only, as a business opportunity and does not recommend any specific policy and investment focus on urban and peri-urban livestock systems. It is of paramount importance that the urbanization of the Livestock Revolution enters the Africa policy agenda, as the sustainability of livestock production systems in the coming decades will depend, to a significant extent, on the development trajectory of livestock production systems in urban and peri-urban areas.
5. Conclusion
For the first time in history, in 2034, more African people are expected to live in cities than in rural areas. In 2050, the African population should reach 2.5 billion people, of which 1.5 billion people will likely live in urban areas. As urbanization keeps advancing, economies expanding and the middle class growing (African Development Bank, 2011), the demand for livestock products is projected to grow substantially if continuation of historical trends of food preferences is assumed and economic growth observed in the early 2000s will keep its pace till 2030 and then get closer to historical long-term rates. Along the years, the bulk of ASF consumption should gradually shift from rural to urban areas and the massive increase and changes in location of ASF consumption are expected to radically transform the livestock value chains.
Although there is uncertainty about how it might evolve, historical evidences from Asia and Latin America suggest that the perishable character of animal products and limited infrastructure will likely induce production to initially locate close to demand. Accordingly, an increase in the number of mid- and large-scale operators in peri-urban areas is to be expected. There will likely be major transformations of livestock production systems in rural areas too and projections picture SSA unable to meet consumers’ demand if current yield trends continue; thus, the food import bill for many African countries is also projected to increase.
In any case, the likely extraordinary concentration of people and livestock in urban and peri-urban areas will pose critical environmental and public health challenges. In particular, land-use change and novel and more frequent interactions between humans, livestock and wildlife will likely create veritable hotspots for the emergence of zoonotic diseases, while high density of animals in urban areas may easily pollute soil, water and air, further exacerbating the negative impact of livestock on public health.
Africa is heterogenous, and so will be the future development of its regions, countries and the multitude of livestock production systems and value chains. However, the urbanization of the Livestock Revolution and its impact on society will be soon become a recurrent theme. Up to date, policy makers have shown little attention to the unfolding of the Livestock Revolution in urban areas. A change of pace is necessary. This should include three core elements. First, the generation of more robust evidences of the coming transformations of livestock sector in and around African urban areas, from any discipline. Second, the adoption of a One Health approach for decision-makers - including not only the Ministries in charge of livestock but also urban planners and city governors - to better appreciate the role of livestock in the urban context and its multiple connections, including trade-offs, with desirable societal outcomes, such as livelihoods, environmental sustainability and public health. Third, the engagement of private sector stakeholders in the design of any policy and public investments targeting the livestock sector. Livestock is a private business and urban areas represent the more lucrative market for livestock entrepreneurs: it is only through engaging private sector in a constructive dialogue that policies can be formulated to create that enabling environment that ensures sustainability from an economic, environmental and public health dimension.
The findings of this paper shed light on the importance of generating a novel policy narrative on livestock sector development in the African continent, which not only includes rural areas but also urban and peri-urban livestock farming and value chain. It is crucial to produce evidence and knowledge to allow an efficient allocation of scarce resources for livestock sector development, which considers the coming changing location of production and consumption of livestock products in the African continent.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This work was financially supported by the United States Agency for International Development (USAID) funded project OSRO/GLO/602/USA (grant number: GHA-G-00-06-00001) implemented by FAO in the context of USAID's Emerging Pandemic Threats Phase II (EPT2) Program. We also would like to thank Mikecz Orsolya for the survey analysis on animal product consumption in selected African countries and Cinardi Giuseppina for a preliminary spatial analysis on human and animal density in and around major African cities.
Annex I
The Livestock Revolution in numbers
Table 3.
Region | Yearly growth rate |
Absolute increase |
||||||
---|---|---|---|---|---|---|---|---|
aggregate consumption |
per capita consumption |
aggregate consumption |
per capita consumption |
|||||
(%) |
(%) |
(1000 metric tons) |
(kg/person) |
|||||
1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | |
Developed | 0.9 | 0.4 | 0.6 | 0.3 | 32612 | 16634 | 17.4 | 9.2 |
Developing | 4.6 | 1.2 | 2.7 | 0.2 | 160913 | 106881 | 21.9 | 2.7 |
Developing (excl. Africa) | 4.7 | 0.9 | 3.0 | 0.4 | 146901 | 68733 | 25.4 | 5.3 |
Africa | 3.5 | 3.0 | 0.8 | 0.6 | 14015 | 38147 | 5.2 | 4.3 |
Northern Africa | 4.2 | 2.0 | 2.0 | 0.6 | 4695 | 6452 | 15.2 | 6.4 |
Sub-Saharan Africa | 3.2 | 3.4 | 0.4 | 0.7 | 9320 | 31696 | 2.5 | 4.8 |
Source: author's elaboration on FAOSTAT and FAO (2018a).
Table 4.
Region | Yearly growth rate |
Absolute increase |
||||||
---|---|---|---|---|---|---|---|---|
aggregate consumption |
per capita consumption |
aggregate consumption |
per capita consumption |
|||||
(%) |
(%) |
(1000 metric tons) |
(kg/person) |
|||||
1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | 1973–2013 | 2013–2050 | |
Developed | 0.6 | 0.3 | 0.3 | 0.2 | 56846 | 28102 | 21.3 | 12.9 |
Developing | 3.8 | 3.2 | 1.9 | 0.2 | 281422 | 208632 | 33.8 | 6.1 |
Developing (excl. Africa) | 3.9 | 1.0 | 2.2 | 0.5 | 249508 | 144256 | 38.5 | 12.8 |
Africa | 3.4 | 2.5 | 0.7 | 0.0 | 31913 | 64376 | 10.9 | 0.4 |
Northern Africa | 4.0 | 1.8 | 1.9 | 0.3 | 15392 | 18270 | 48.5 | 12.5 |
Sub-Saharan Africa | 2.9 | 2.9 | 0.2 | 0.2 | 16522 | 46106 | 2.0 | 2.9 |
Source: author's elaboration on FAOSTAT and FAO (2018a).
Annex II
Summary statistics on small ruminant meat expenditure
Table 5.
quantiles ofGDP per capita |
average |
average |
average |
RuraltoUrban ratio |
---|---|---|---|---|
GDP per capita |
Rural per capita expenditure |
Urban per capita expenditure |
||
2011 PPP (current international $) | 2011 PPP (current international $) | 2011 PPP (current international $) | ||
1 | 1224 | 6 | 10 | 0.78 |
2 | 2717 | 15 | 18 | 0.7 |
3 | 5137 | 9.1 | 12 | 1 |
4 | 8504 | 17 | 16 | 1.3 |
5 |
14624 |
11 |
21 |
1.2 |
quantiles of urban share |
average |
average |
average |
Rural toUrban ratio |
GDP per capita |
Rural per capita expenditure |
Urban per capita expenditure |
||
2011 PPP (current international $) |
2011 PPP (current international $) |
2011 PPP (current international $) |
||
1 | 2755 | 6.9 | 10 | 1.1 |
2 | 2814 | 11 | 14 | 0.66 |
3 | 5887 | 5.6 | 7.7 | 0.91 |
4 | 8383 | 15 | 15 | 1.3 |
5 | 12215 | 20 | 31 | 1.1 |
Source: author's elaboration on Global Consumption Database (World Bank, 2007)
Annex III
Consumption of ASFs in urban and rural areas, 2015–2050
Table 6.
Beef and Veal (kg/person/year) |
Pork (kg/person/year) |
Poultry meat (kg/person/year) |
Small ruminant meat (kg/person/year) |
Milk (kg/person/year) |
||||||
---|---|---|---|---|---|---|---|---|---|---|
rural | urban | rural | urban | rural | urban | rural | urban | rural | urban | |
Africa | ||||||||||
2015 | 4.9 | 9.4 | 1.3 | 1.8 | 4.1 | 10.2 | 2.9 | 2.8 | 33.1 | 57.9 |
2050 | 6.4 | 11.4 | 2.1 | 2.5 | 4.9 | 9.8 | 3.8 | 3.3 | 33.8 | 49.9 |
Northern Africa | ||||||||||
2015 | 7.4 | 11.9 | 0.0 | 0.0 | 8.4 | 14.4 | 5.0 | 4.5 | 72.8 | 123.3 |
2050 | 10.7 | 15.2 | 0.0 | 0.0 | 11.5 | 17.0 | 6.2 | 5.4 | 77.5 | 120.3 |
Sub-Saharan Africa | ||||||||||
2015 | 4.4 | 8.7 | 1.5 | 2.4 | 3.3 | 8.9 | 2.5 | 2.3 | 25.7 | 37.5 |
2050 | 5.8 | 10.7 | 2.3 | 2.9 | 3.9 | 8.4 | 3.4 | 2.9 | 27.5 | 36.9 |
Annex IV
Sensitivity analysis
Table 7.
Area | year | Meat (%) |
Milk (%) |
---|---|---|---|
Africa | 2013 | 12.04 | 16.61 |
Northern Africa | 2013 | 8.10 | 19.95 |
Sub-Saharan Africa | 2013 | 13.80 | 13.83 |
Brazil | 2003 | 0.45 | 1.89 |
India | 2005 | 0.01 | 0.01 |
Source: author's elaboration on FAO data (2018c)
Table 8.
Area | |||
---|---|---|---|
Product | Africa | Northern Africa | Sub-Saharan Africa |
Beef and veal | |||
equal price | 72.1% | 71.5% | 72.2% |
urban price 3% higher | 71.5% | 70.9% | 71.7% |
urban price 10% higher | 70.2% | 69.6% | 70.4% |
Poultry meat | |||
equal price | 74.4% | 72.5% | 75.2% |
urban price 3% higher | 73.9% | 71.9% | 74.6% |
urban price 10% higher | 72.7% | 70.6% | 73.4% |
Pork | |||
equal price | 63.4% | 58.2% | 63.4% |
urban price 3% higher | 62.7% | 57.5% | 62.7% |
urban price 10% higher | 61.2% | 56.0% | 61.3% |
Small ruminant meat | |||
equal price | 55.5% | 61.0% | 53.8% |
urban price 3% higher | 54.9% | 60.4% | 53.2% |
urban price 10% higher | 53.4% | 58.9% | 51.7% |
Meat | |||
equal price | 69.5% | 70.2% | 69.3% |
urban price 3% higher | 68.9% | 69.6% | 68.7% |
urban price 10% higher | 67.6% | 68.3% | 67.4% |
Milk | |||
equal price | 68.1% | 73.4% | 65.2% |
urban price 3% higher | 67.5% | 72.8% | 64.6% |
urban price 10% higher | 66.1% | 71.6% | 63.2% |
Annex V
Share of consumption of milk and meat purchased in rural and urban areas
Annex VI
GDP per capita and urban population in African and Asian regions
Annex VII
Regional classification
Table 9.
Table 10.
region | country | 2012 population (thousands) | share of African population |
---|---|---|---|
Western | Cabo Verde | 514 | 0.05% |
Southern | Comoros | 724 | 0.07% |
Central | Equatorial Guinea | 1039 | 0.09% |
Eastern | Djibouti | 881 | 0.08% |
Western | Guinea-Bissau | 1638 | 0.15% |
Central | Sao Tome and Principe | 183 | 0.02% |
Southern | Seychelles | 92 | 0.01% |
Northern | Western Sahara | 496 | 0.04% |
tot | 5567 | 0.50% | |
African population | 1,104,216 |
References
- Abdulai A., Aubert D. A cross-section analysis of household demand for food and nutrients in Tanzania. Agric. Econ. 2004:67–79. doi: 10.1016/j.agecon.2003.03.001. [DOI] [Google Scholar]
- Abdulrahman S., Mani J.R., Oladimeji Y.U., Abdulazeez R.O., Ibrahim L.A. Analysis of entrepreneural management and food security strategies of small ruminants women farmers in kirikassamma local government area of jigawa state. J. Anim. Prod. Res. 2017;29:419–429. [Google Scholar]
- African Development Bank . AfDB; Tunis: 2011. Africa in 50 Years' Time - the Road towards Inclusive Growth. [Google Scholar]
- African Union . Inter-African Bureau for Animal Resources; Nairobi: 2015. The Livestock Development Strategy for Africa (LiDeSA) 2015-2035. [Google Scholar]
- Akaike H. Nformation theory and an extension of the maximum likelihood principle. In: Petrov B.N., Caski F., editors. Proceedings of the Second International Symposium on Information Theory. Akademiai Kiado; Budapest: 1973. [Google Scholar]
- Amadou H., Dossa L.H., Lompo D.J., Abdulkadir A., Schlecht E. A comparison between urban livestock production strategies in Burkina Faso, Mali and Nigeria in West Africa. Trop. Anim. Health Prod. 2012;44(7):1631–1642. doi: 10.1007/s11250-012-0118-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Ayano Ogawa V.M. Readiness for 2030. National Academies of Sciences, Engineering, and Medicine. The National Academic Press; Washington D.C.: 2019. Exploring lessons learned from a century of outbreaks. [DOI] [PubMed] [Google Scholar]
- Berry K., Allen T., Horan R.D., Shogren J.F., Finnoff D., Daszak P. The economic case for a pandemic fund. EcoHealth. 2018;15:244–258. doi: 10.1007/s10393-018-1338-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Breusch T., Pagan A. A simple test for heteroskedasticity and random coefficient variation. Econometrica. 1979;47(5):1287–1294. doi: 10.2307/1911963. [DOI] [Google Scholar]
- Bright E.A., Coleman P.R., King A.L., Rose A.N., Urban M.L. Oak Ridge National Laboratory; Oak Ridge, TN: 2009. LandScan 2008. [Google Scholar]
- Bright E.A., Coleman P.R., Rose A.N., Urban M.L. Oak Ridge National Laboratory; Oak Ridge, TN: 2010. LandScan 2009. [Google Scholar]
- Chamberlin J., Jaybe T. Unpacking the meaning of ‘market access’: evidence from rural Kenya. World Dev. 2013;41(C):245–264. doi: 10.1016/j.worlddev.2012.06.004. [DOI] [Google Scholar]
- Cnfa . USAID; 2016. USAID REGIS-AG Small Ruminant Value Chain and End Market Assessment. [Google Scholar]
- Cockx L., Colen L., De Weerdt J. From corn to popcorn? Urbanization and dietary change: evidence from rural-urban migrants in Tanzania. World Dev. 2018;110:140–159. doi: 10.1016/j.worlddev.2018.04.018. [DOI] [Google Scholar]
- Cole D., Lee-Smith D., Nasinyama G. CIP/Urban Harvest and Makerere University Press; Lima, Peru: 2008. Healthy City Harvests: Generating Evidence to Guide Policy on Urban Agriculture. [Google Scholar]
- Colen L., Melo P., Abdul-Salam Y., Roberts D., Mary S., Gomez Y Paloma S. Income elasticities for food, calories and nutrients across Africa: a meta-analysis. Food Pol. 2018;77:116–132. doi: 10.1016/j.foodpol.2018.04.002. [DOI] [Google Scholar]
- Deaton A., Dupriez O. Working Paper 1321, Research Program in Development Studies. Woodrow Wilson School of Public and International Affairs, Princeton University; Princeton, NJ: 2011. Spatial price differences within large countries. [Google Scholar]
- Delgado C., Rosegrant M., Meijer S. Paper Presented at the International Trade Research Consortium. Auckland, New Zeland. 2001. Livestock to 2020: the revolution continues. [Google Scholar]
- Delgado C., Rosegrant M., Steinfeld H., Ehui S., Courbois C. Food, Agriculture, and the Environmental Discussion Paper(28) 1999, May. Livestock to 2020. The next food revolution. [Google Scholar]
- Delisle H., Ntandou-Bouzitou G., Agueh V., Sodjinou R., Fayomi B. Urbanisation, nutrition transition and cardiometabolic risk: the Benin study. Br. J. Nutr. 2012;107(10):1534–1544. doi: 10.1017/S0007114511004661. [DOI] [PubMed] [Google Scholar]
- Duncan A.J., Teufel N., Mekonnen K., Singh V.K., Bitew A., Gebremedhin B. Dairy intensification in developing countries: effects of market quality on farm-level feeding and breeding practices. Animal. 2013;7(12):2054–2062. doi: 10.1017/S1751731113001602. [DOI] [PMC free article] [PubMed] [Google Scholar]
- FAO . FAO; Rome, Italy: 2013. World Livestock 2013. Changing Diseases Landscapes. [Google Scholar]
- FAO . 2018. The Future of Food and Agriculture – Alternative Pathways to 2050. Rome. [Google Scholar]
- FAO FAOSTAT - commodity balances - livestock and fish primary equivalent. 2018, January 17. http://www.fao.org/faostat/en/#data/BL Retrieved August 5, 2019, from.
- FAO FAOSTAT - trade crops and livestock products. 2018, June 28. http://www.fao.org/faostat/en/#data/TP Retrieved Septemeber 2019, from.
- FAO RuLIS - rural livelihoods information system. 2020. http://www.fao.org/in-action/rural-livelihoods-dataset-rulis/en/ Retrieved April 2020, from.
- Gaddis I. Policy Research Working Paper 7652. World Bank; Washington, DC: 2016, April. Prices for poverty analysis in Africa. [Google Scholar]
- Gibson J. Working Paper 64273. World Bank; Washington, DC: 2009. Regional price deflators for VHLSS 2008-2010 and GSO capacity building for spatial cost of living index. [Google Scholar]
- Global Human Settlement Layer (GHSL) JRC; 2008. European Commission, Joint Research Centre. [Google Scholar]
- Global Human Settlement Layer (GHSL) JRC; 2009. European Commission, Joint Research Centre. [Google Scholar]
- Grace D., Lindahl J., Correa M., Kakkar M. Urban livestock keeping. In: de Zeeuw H., Drechsel P., editors. Cities and Agriculture - Developing Resilient Urban Food Systems. Routledge; Oxford, UK: 2015. pp. 255–284. [Google Scholar]
- Graefe S., Schlecht E., Buerkert A. Opportunities and challenges of urban and peri-urban agriculture in niamey, Niger. Outlook Agric. 2008;37(1):47–56. doi: 10.5367/000000008783883564. [DOI] [Google Scholar]
- Hassell J.M., Begon M., Ward M.J., Fèvre E.M. Urbanization and disease emergence: dynamics at the wildlife-livestock-human interface. Trends Ecol. Evol. 2017;32(1):55–67. doi: 10.1016/j.tree.2016.09.012. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Hawkes C. Dietary implications of supermarket development: a global perspective. Dev. Pol. Rev. 2008;26(6):657–692. doi: 10.1111/j.1467-7679.2008.00428.x. [DOI] [Google Scholar]
- Huber P.J. Proceedings of the Fifth Berkeley Symposium on Mathematical Statistics and Probability. University of California Press; Berkeley: 1967. The behavior of maximum likelihood estimates under nonstandard conditions; pp. 221–233. [Google Scholar]
- Jones K.E., Patel N.G., Levy M.A., Storeygard A., Balk D., Gittleman J.L., Daszak P. Global trends in emerging infectious diseases. Nature. 2008;451(7181):990–993. doi: 10.1038/nature06536. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kavallari A., Conforti P., Mensbrugghe D. ESA Working Paper(16-06) 2016, September. The global agriculture perspectives system (GAPS) version 1.0. [Google Scholar]
- Kenya National Bureau of Statistics . Livestock Population by Type and District; 2009. Population and Housing Census 2009. [Google Scholar]
- Lee-Smith D. Cities feeding people: an update on urban agriculture. Environ. Urbanization. 2010;22(2):483–499. doi: 10.1177/0956247810377383. [DOI] [Google Scholar]
- Mensbrugghe D. The World Bank; 2010, December. Environmental Impact and Sustainability Applied General Equilibrium (ENVISAGE) Model Version 7.1. [Google Scholar]
- Migose S.A., Bebe B.O., de Boer I., Oosting S.J. Influence of distance to urban markets on smallholder dairy farming systems in Kenya. Trop. Anim. Health Prod. 2018;50(7):1417–1426. doi: 10.1007/s11250-018-1575-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Muhammad I.R. Livestock ownership and unconventional feed resources from refuse dumps in urban metropolis of semi arid zone. Res. J. Anim. Sci. 2008;2(1):12–16. [Google Scholar]
- Nakamura S., Harati R., Lall S., Dikhanov Y., Hamadeh N., Oliver W.V. Is living in african cities expensive? Appl. Econ. Lett. 2019;26(12):1007–1012. doi: 10.1080/13504851.2018.1527441. [DOI] [Google Scholar]
- Neiderud C. How urbanization affects the epidemiology of emerging infectious diseases. Infect. Ecol. Epidemiol. 2015;5(1) doi: 10.3402/iee.v5.27060. [DOI] [PMC free article] [PubMed] [Google Scholar]
- OECD-FAO . OECD; Paris: 2009. OECD-FAO Agricultural Outlook 2009. [Google Scholar]
- Oosting S.J., Udo H.M., Viets T.C. Development of livestock production in the tropics: farm and farmers' perspectives. Animal. 2014;8(8):1238–1248. doi: 10.1017/S1751731114000548. [DOI] [PubMed] [Google Scholar]
- Pica-Ciamarra U., Otte J. The 'Livestock Revolution': rethoric and reality. Outlook Agric. 2011;40(1):7–19. doi: 10.5367/oa.2011.0030. [DOI] [Google Scholar]
- Rae A.N. The effects of expenditure growth and urbanisation on food consumption in East Asia: a note on animal products. Agric. Econ. 1998;18(3):291–299. doi: 10.1016/S0169-5150(97)00051-0. [DOI] [Google Scholar]
- Regmi A., Dyck J. Effects of urbanization on global food demand. In: Regmi A., editor. Changing Structure of Global Food Consumption and Trade. Economic Research Service/USDA; 2001. [Google Scholar]
- Robinson T.P., Bu D.P., Carrique-Mas J., Fèvre E.M., Gilbert M., Grace D. Antibiotic resistance: mitigation opportunities in livestock sector development. Animal. 2017;11(1):1–3. doi: 10.1017/S1751731116001828. [DOI] [PubMed] [Google Scholar]
- Schwarz G. Estimating the dimension of a model. Ann. Stat. 1978;6:461–464. [Google Scholar]
- Seto K.C., Ramankutty N. Hidden linkages between urbanization and food systems. Science. 2016;352(6288):943–945. doi: 10.1126/science.aaf7439. [DOI] [PubMed] [Google Scholar]
- Skoufias E., Di Maro V., González-Cossío T., Rodríguez Ramirez S. Food quality, calories and household income. Appl. Econ. 2011;43(28):4331–4342. doi: 10.1080/00036846.2010.491454. [DOI] [Google Scholar]
- Steinfeld H., Gerber P., Wassenaar T., Castel V., Rosales M., de Haan C. FAO; Rome: 2006. Livestock's Long Shadow. Environmental Issues and Options. [Google Scholar]
- Steinfeld H.R.T.-C. Molecules, money, and microbes. In: Campanhola C.a., editor. Sustainable Food and Agriculture. An Integrated Approach. Academic Press; Cambridge, MA, USA: 2019. p. 594. [Google Scholar]
- Thornton P.K. Livestock production: recent trends, future prospects. Philos. Trans. R. Soc. Lond. B Biol. Sci. 2010;365(1554):2853–2867. doi: 10.1098/rstb.2010.0134. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Uganda Bureau of Statistics . Uganda National Data Archive; 2010, May. National Livestock Census 2008 (NLC 2008) [Google Scholar]
- UNDESA . United Nations; New York: 2018. United Nations Demographic Yearbook. [Google Scholar]
- UNDESA, Population Division . Online Edition. 2018. World Urbanization Prospects: the 2018 Revision. [Google Scholar]
- Verbeek M. Interpreting and comparing regression models. In: Veerbek M., editor. A Guide to Modern Econometrics. third ed. John Wiley & Sons Ltd; 2008. [Google Scholar]
- Weiss D.J., Nelson A., Gibson H.S., Temperley W., Peedell S., Lieber A. A global map of travel time to cities to assess inequalities in accessibility in 2015. Nature. 2018, January 18;553:333–336. doi: 10.1038/nature25181. doi: 10.1038/nature25181. [DOI] [PubMed] [Google Scholar]
- White H. A heteroskedasticity-consistent covariance matrix estimator and a direct test for heteroskedasticity. Econometrica. 1980;48:817–838. [Google Scholar]
- Worku I.H., Dereje M., Minten B., Hirvonen K. Diet transformation in Africa: the case of Ethiopia. Agric. Econ. 2017;48(S1):73–86. Diet transformation in Africa: the case of Ethiopia. [Google Scholar]
- World Bank Global consumption database. 2007. http://datatopics.worldbank.org/consumption/ Retrieved April 2019, from.
- World Bank International LPI - country score card. 2019. lpi.worldbank.org Retrieved from.